• Category
  • Length Range
    18-40 µm
  • Width Range
    9-20 µm
  • Striae in 10 µm
    22-24 in center valve
  • Synonyms
    Achnanthes flexella (Kütz.) Brun

Identification

Description

Frustules are strongly bent in girdle view with concave raphe valve and convex rapheless valve. Valves are elliptical-lanceolate with slightly drawn-out ends and deep mantles. Valve face has depressions along the margins. The raphe valve has a narrow axial area and a lanceolate-rhomboid central area. The raphe is straight or slightly sigmoid with terminal ends sharply turned to opposite directions. Rapheless valve has a narrow linear or slightly sigmoid axial area and a large rectangular or hexagonal central area. The striae are punctate, strongly radiate on raphe valve and slightly radiate on rapheless valve, 22-24 in 10 μm.

Autecology

This taxon has been reported with light micrographs from Alaska (Foged 1981), the northeastern US (Camburn and Charles 2000), northern Québec, Labrador (Fallu et al. 2000), Rocky Mountains, Cascades, and Olympic Mountains (Bahls 2021). It has been reported from streams of the west (EPA Western EMAP, USGS Regional Survey of California) and lakes of the northeast (EPA Northeast Lake Survey).

In the Great Lakes National Parks (Edlund et al. 2009, 2011, 2012, 2013), this taxon is common (1-5% abundance) in sediment core material from Sleeping Bear Dunes (Shell Lake). and rare (0.1-1% abundance) at Pictured Rocks (Grand Sable and Beaver lakes), Sleeping Bear Dunes (Manitou, Bass, and Florence lakes), Voyageurs (Cruiser, Ek, Little Trout, Locator lakes), and Isle Royale (Richie).

This taxon is known to occur in mountainous lakes, ponds, rivers and streams with cool waters of low conductivity and nutrient content (Bahls 2021). This taxon's pH preference is unclear (Patrick and Reimer 1966, Camburn and Charles 2000, Antoniades et al. 2008, Bahls 2021). This diatom is small in size and typically grows attached to surfaces in a prostrate manner. Cells are only slightly motile and grow as single cells (they do not form colonies). In California, this taxon is characterized within the Biological Condition Gradient (BCG) of 2, which are highly sensitive species.

Many research groups consider this taxon an indicator organism and published regional environmental optima and tolerances including:

Camburn and Charles (2000): pH - 6.66 +/- 0.78, Acid Neutralizing Capacity - 114 +/- 168 µeq/L, Total Aluminum - 107 +/- 46 µg/L, Dissolved Organic Carbon (DOC) - 382 +/- 212 µmol/L, Total Phosphorus - 6.13 +/- 3.20 µg/L for populations from the Northeastern US.

Fallu et al. (2000): DOC - 8.72 +/- 1.39 mg/L, Color - 13 +/- 2.7 Pt units, Alkalinity - 45 +/- 2.8 µeq/L for populations from northern Québec and Labrador.

Antoniades et al. (2008): pH - 8.0, Tolerance Range - 7.4-8.6, Conductivity - 128 µS/cm, Tolerance Range - 63-260 µS/cm, Dissolved Organic Carbon - 3.16 mg/L, Tolerance Range - 1.28-7.76 µS/cm for populations from the Canadian Arctic Archipelago. Note that the authors included E. leptostriata in their counts for E. flexella.

Bahls (2021): Conductivity - 224 µS/cm, pH - 7.9, Temperature - 13.8°C, Total Nitrogen - 0.19 mg/L, Total Phosphorus - 5 µg/L for populations in the Rocky Mountains, Cascades and Olympic Mountains.

Original Description

CYMBELLA? FLEXELLA. Taf. 4. Fig. XIV, Taf. 6. Fig. VIII. (420/1). C. laevissima, mi¬nor, a latere secundario elliptica, subsigmoidea, apicibus parum productis obtusis, altero latere cur-vata, (genuflexa) dorso convexo, ventre concavo exciso, apice truncato. In Quellwasser bei Thun in der Schweiz! — Länge 1/55"'.

  • Basionym
    Cymbella flexella
  • Author
    Kütz. 1844
  • Length Range
    41 µm

Original Images

Orig Ill 1 1
Orig Ill 2

Citations & Links

Citations

Links

  • Index Nominum Algarum
  • North American Diatom Ecological Database
    NADED ID: 187001

Updates

Feb 05, 2026 - Addition of Autecology

From 2010 until 2026, the autecological information on this taxon page was limited. As of this update, information on ecology, biogeography, and environmental optima have been added. - Lane Allen and Mark Edlund

Cite This Page

Potapova, M., Edlund, M., Allen, L. (2010). Eucocconeis flexella. In Diatoms of North America. Retrieved February 17, 2026, from https://diatoms.org/species/44846/eucocconeis_flexella

Responses

The 15 response plots show an environmental variable (x axis) against the relative abundance (y axis) of Eucocconeis flexella from all the stream reaches where it was present. Note that the relative abundance scale is the same on each plot. Explanation of each environmental variable and units are as follows:

ELEVATION = stream reach elevation (meters)
STRAHLER = distribution plot of the Strahler Stream Order
SLOPE = stream reach gradient (degrees)
W1_HALL = an index that is a measure of streamside (riparian) human activity that ranges from 0 - 10, with a value of 0 indicating of minimal disturbance to a value of 10 indicating severe disturbance.
PHSTVL = pH measured in a sealed syringe sample (pH units)
log_COND = log concentration of specific conductivity (µS/cm)
log_PTL = log concentration of total phosphorus (µg/L)
log_NO3 = log concentration of nitrate (µeq/L)
log_DOC = log concentration of dissolved organic carbon (mg/L)
log_SIO2 = log concentration of silicon (mg/L)
log_NA = log concentration of sodium (µeq/L)
log_HCO3 = log concentration of the bicarbonate ion (µeq/L)
EMBED = percent of the stream substrate that is embedded by sand and fine sediment
log_TURBIDITY = log of turbidity, a measure of cloudiness of water, in nephelometric turbidity units (NTU).
DISTOT = an index of total human disturbance in the watershed that ranges from 1 - 100, with a value of 0 indicating of minimal disturbance to a value of 100 indicating severe disturbance.